Recent interest in characterizing methyl bromide emission has focused
on field and laboratory measurements, which are expensive to conduct a
nd very time consuming. Predicting methyl bromide volatilization with
numerical or analytical models has been limited to idealized situation
s without considering environmental conditions such as diurnal tempera
ture change. It has been found that temperature can strongly affect me
thyl bromide volatilization under field conditions. To quantitatively
characterize temperature effect, we adopted a two-dimensional numerica
l model that can solve simultaneous equations of water, heat, and solu
te transport (including both liquid and vapor phases). Functional rela
tionships were established between temperature and methyl bromide liqu
id-gas phase partition coefficient or the Henry's constant, diffusion
coefficient in soil air space, and the permeability of polyethylene ta
rp. To test the model, soil properties and boundary conditions from Ya
tes et al. (1996 a,b,c) were used. The model prediction was completely
independent of the field measurement. The model simulation by conside
ring diurnal variations of soil temperature predicted the cumulative e
mission that agreed well with the measured flux density. Prediction wi
thout considering temperature missed the diurnal nature in emission fl
ux density. Comparable results were also obtained for methyl bromide c
oncentration in the soil profile. The key advantage of this model is i
ts ability of describing diurnal variations in methyl bromide emission
flux. Based on the temperature effect on temporal variations of methy
l bromide emission, we believe that small sampling intervals are neede
d to determine the dynamic nature of methyl bromide emission under fie
ld conditions, especially during the first 24 h after application.